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EC number: 215-114-8 | CAS number: 1303-00-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Immunotoxicity
Administrative data
Description of key information
The reliable studies, especially the 14-week and 2-year inhalation toxicity studies with rats and mice, showed no immunotoxic action of GaAs and there are no hints for an immunotoxic action of GaAs.
The NTP inhalation toxicity studies revealed that GaAs causes a sort of local inflammation at the exposure site (lung) which is in line with the observed significant increase of the number of segmented neutrophils and is considered as a reaction of the immune system rather than a toxic action to the immune system.
This is only true for inhalative exposure. Oral or dermal exposure to GaAs is tolerated without observable toxicity.
Key value for chemical safety assessment
Additional information
There exist 29 not reliable studies or not assignable studies related to immunotoxicity of GaAs. Their results are ignored for the evaluation.
The results from fully reliable studies, especially the results of the 2-year inhalation toxicity studies with rats and mice, revealed that relatively low concentrations of GaAs in the air (i.e. 0.01 mg GaAs/m³) caused an inflammation in the lung after repeated exposure. Additionally in these studies a complete histopathology was performed on the lymph nodes (bronchial, mandibular, mediastinal, mesenteric), on the spleen and the thymus of all animals. No test article related effects were found in these organs.
Hematology data for immune system relevant cells such as the leukocytes (segmented neutrophils, lymphocytes, monocytes and eosinophils) were available for different GaAs concentrations in the the fully reliable 14-week inhalation studies on mice and rats (NTP, 2000). Except for the segmented neutrophils, no significant changes in the number of these cells have been observed after 14 weeks of GaAs exposure in female and male rat and mice. These data do not give a hint to any functional impairments of the immunsystem caused by GaAs. The observed significant increase of the number of segmented neutrophils is in line with the observed local inflammation at the exposure site (lung).
Hence, the reliable studies, especially the 14-week and 2-year inhalation toxicity studies with rats and mice, showed no immunotoxic action of GaAs.
Although in summary not reliable a study of Becker and McCoy (2003) seems to give in one part consistent results:
Becker and McCoy investigated in a ribonuclease protection assay 25 different cytokines of splenocytes and peritoneal residential cells. Mice were administered a single intraperitoneal dose of 200 mg GaAs/ kg bw.. At 6, 18, and 48 hours after exposure blood was collected, resident peritoneal leukocytes were harvested by lavage and splenic cell suspensions were prepared. Total RNA was prepared and analysed using the RiboQuant Multi-Probe Ribinuclease Protection Assay System. The MultiProbe assessed a panel of 25 different cytokines. 17 mRNA encoding for cytokines implicated in promoting inflammation and leukocyte taxis were detected at significantly higher levels than after vehicle treatment, while 3 anti-inflammatory cytokines were diminished to below detection limit. This set of experiments seems to show consistent results and supports the findings of the NTP inhalation toxicity studies that GaAs causes a local inflammation at the exposure site (lung). This is only true for inhalation exposure. Oral or dermal exposure to GaAs are tolerated without observable toxicity.
Justification for classification or non-classification
The reliable studies, especially the 2 -year study with rats and mice, showed no immunotoxic action of GaAs.
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